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Notes from the Field
Michael Josselyn, PhD, PWS
PhD in Botany 1978

Professor at San
Francisco State
University 1978-2000

Initiated research on
tidal wetland restoration

Founded company
focused on restoration
and mitigation projects
It is easy to create a marsh;
      it is hard to create a wetland system
Restoration is not just a science or an art;
     it is the practical application of
     knowledge
Mitigation is a regulatory outcome;
     its success is a function of policy
     decisions
Time is your friend; as long as it doesn’t run
     out
Clean Water Act
Wetlands defined by
presence of obligate
wetland plants
Focus on tidal marsh
restoration using
dredged materials
Spartina was king
Little interest in drier
end wetlands
Placement of
dredged materials
critical
• Too high: acid soil
  conditions
• Too low: no vegetation
  establishment
Focused on
vegetation
establishment as
primary criteria
Tidal channels
improve habitat
function
Tidal energy
necessary to form
channels
High marsh areas
have slower channel
formation
Muzzi Marsh after 20 years—natural revegetation by cordgrass
after sedimentation occurred also gives rise of natural channel
                                                  configuration
                                    Williams and Faber (2001)
Most marsh species
found above 60%
exposed
Pickleweed marsh
found 80% or greater
Development and use of tidal gates can provide the same
 exposure frequencies so that vegetated marshes can be
            established in subsided lands behind levees
FWS wetland inventory and “community
  profiles” of wetland types
• Recognizes seasonal hydrology subtypes
Corps adopts 87 Delineation Manual
• 5-12 % of the growing season for wetland hydrology
Mitigation becomes an essential
  element of permitting
“Nothing is working”
• Race (1983) 90% of the restoration sites are failures
• Kusler et al (1989) compliance vs functional success
• Vernal pools, diked wetlands; seasonal
        wetlands
• Mitigation needs to reflect new
        hydrology standard
• Most previous projects focused
        only on obligate wetland
        species
Josselyn et al 1990
Mitigation for drier wetlands needs to consider saturation over
                               3 month period in growing season
( development of anaerobic conditions takes longer than 7 days)
Kusler and Kentula (1990)
• Partial failures common
• Success varies by type of wetland and functions
• Short and long-term success different
• Multidiscplinary expertise required
• Clear and specific goals for mitigation projects
National Research Council (1991)
• Strive to restore self sustaining systems
• Develop innovative methods to accelerate
  restoration
• Support experimental research in restoration
No net loss policy initiated by federal
and state agencies
• Mitigation ratios increase
Assessment methods to evaluate wetland
success on functional basis
Complex ecosystems being designed as
mitigation
Vernal pool restoration technology
improving
Permits issued between
1988-1994 by Corps in
California total over 3100

Most required wetland
mitigation/restoration

Most required 5 year
monitoring
In-kind mitigation

Creation given highest
priority

More acreage than
impacted

Success in 5 years

Complete at low cost
National Research Council 2001   Percent Successful
Mitigation for Port Fill
                                        [650 acres mitigation]
                                        Restoration of tidal
                                        inlet
                                        Dredging of fine
                                        sediments
                                        Creation of shorebird
                                        nesting islands
                                        Planting of emergent
                                        and submerged
                                        vegetation

Courtesy: Merkel and Associates, 2009
Fears that Port was destroying existing
habitat for shorebirds

Dredging project was too big and would
be destructive to existing coastal
vegetated wetland and endangered
species

Federal and State Courts ruled against
ESA and CEQA challenges
Revegetation
successful

Cordgrass
and eelgrass
increase
unexpected

Decline in
intertidal
mudflats
               Courtesy: Merkel and Associates, 2009
COMPARED TO OTHER
 FISH SPECIES NUMBER
                                                                              LAGOONS


            N um ber o f Fish Species W ith in Bat iquit o s Lagoo n
50
45
40
35
30
25
20
15
10
5
0
     1984   1994   1996   1997    1998   1999   2001    2003   2005    2006




                                                                                  Courtesy: Merkel and Associates, 2009
Shorebirds




Light footed clapper rail




             Photo: Monte Stinnett




                                     Courtesy: Merkel and Associates, 2009
Courtesy: Merkel and Associates, 2009
Restoring entire ecosystems requires patience and acceptance
                                      that habitats will evolve.
   Change is inevitable and management needs to be flexible.
Mitigation for
commercial
development in
Fremont, CA
Degraded seasonal
wetlands on former
agricultural lands
Required restoration
of natural vernal pool
landscape
Development next to
US FWS Refuge
Two listed species
with restricted
distribution
• VPTS and CC
  Goldfields
Focused attention by
conservation groups
Demonstrate
feasibility of
establishing tadpole
shrimp habitat
Strict performance
standards for
hydrology and
vegetation
Implement grazing
program
INCREASED VP PLANT SPECIES   IMPROVED OVER TIME
Threshold requirements as performance standards do not
                           recognize natural variability.
                                 Cows are your friends.
Corps adopts compensatory mitigation
policies
Mitigation banks become of age
Stormwater and
LID wetlands
Climate change
affects
everything
Issued by Corps of Engineers: April 2008
• Sets forth regulations for mitigation compliance
Mitigation banking given preference
• Followed by in-lieu fee and permittee-
 responsible mitigation
Sets forth 12 fundamental components for
mitigation plans
Emphasis replacement in watershed
Provides for functional assessment
BEFORE   AFTER
Our knowledge of wetland systems including plants, soils, and
hydrology is providing the basis for a sophisticated design and
       public use of wetland systems in the urban environment
Wetland restoration can achieve successful
outcomes but usually not as expected

Linkage between hydrology, soils, and
plants is better known and allows for more
sophisticated designs of drier wetlands

Wetland restoration will necessarily
become more complex as our demand on
wetland performance increases
Time is of the
essence

Pressure on wetlands
is increasing

Need for large scale
restoration is
unprecedented and
immediate
Sws  Josselyn Presentation

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Sws Josselyn Presentation

  • 1. Notes from the Field Michael Josselyn, PhD, PWS
  • 2. PhD in Botany 1978 Professor at San Francisco State University 1978-2000 Initiated research on tidal wetland restoration Founded company focused on restoration and mitigation projects
  • 3. It is easy to create a marsh; it is hard to create a wetland system Restoration is not just a science or an art; it is the practical application of knowledge Mitigation is a regulatory outcome; its success is a function of policy decisions Time is your friend; as long as it doesn’t run out
  • 4. Clean Water Act Wetlands defined by presence of obligate wetland plants Focus on tidal marsh restoration using dredged materials Spartina was king Little interest in drier end wetlands
  • 5. Placement of dredged materials critical • Too high: acid soil conditions • Too low: no vegetation establishment Focused on vegetation establishment as primary criteria
  • 6. Tidal channels improve habitat function Tidal energy necessary to form channels High marsh areas have slower channel formation
  • 7. Muzzi Marsh after 20 years—natural revegetation by cordgrass after sedimentation occurred also gives rise of natural channel configuration Williams and Faber (2001)
  • 8. Most marsh species found above 60% exposed Pickleweed marsh found 80% or greater
  • 9. Development and use of tidal gates can provide the same exposure frequencies so that vegetated marshes can be established in subsided lands behind levees
  • 10. FWS wetland inventory and “community profiles” of wetland types • Recognizes seasonal hydrology subtypes Corps adopts 87 Delineation Manual • 5-12 % of the growing season for wetland hydrology Mitigation becomes an essential element of permitting “Nothing is working” • Race (1983) 90% of the restoration sites are failures • Kusler et al (1989) compliance vs functional success
  • 11. • Vernal pools, diked wetlands; seasonal wetlands • Mitigation needs to reflect new hydrology standard • Most previous projects focused only on obligate wetland species
  • 13. Mitigation for drier wetlands needs to consider saturation over 3 month period in growing season ( development of anaerobic conditions takes longer than 7 days)
  • 14. Kusler and Kentula (1990) • Partial failures common • Success varies by type of wetland and functions • Short and long-term success different • Multidiscplinary expertise required • Clear and specific goals for mitigation projects National Research Council (1991) • Strive to restore self sustaining systems • Develop innovative methods to accelerate restoration • Support experimental research in restoration
  • 15. No net loss policy initiated by federal and state agencies • Mitigation ratios increase Assessment methods to evaluate wetland success on functional basis Complex ecosystems being designed as mitigation Vernal pool restoration technology improving
  • 16. Permits issued between 1988-1994 by Corps in California total over 3100 Most required wetland mitigation/restoration Most required 5 year monitoring
  • 17. In-kind mitigation Creation given highest priority More acreage than impacted Success in 5 years Complete at low cost
  • 18. National Research Council 2001 Percent Successful
  • 19.
  • 20. Mitigation for Port Fill [650 acres mitigation] Restoration of tidal inlet Dredging of fine sediments Creation of shorebird nesting islands Planting of emergent and submerged vegetation Courtesy: Merkel and Associates, 2009
  • 21. Fears that Port was destroying existing habitat for shorebirds Dredging project was too big and would be destructive to existing coastal vegetated wetland and endangered species Federal and State Courts ruled against ESA and CEQA challenges
  • 23. COMPARED TO OTHER FISH SPECIES NUMBER LAGOONS N um ber o f Fish Species W ith in Bat iquit o s Lagoo n 50 45 40 35 30 25 20 15 10 5 0 1984 1994 1996 1997 1998 1999 2001 2003 2005 2006 Courtesy: Merkel and Associates, 2009
  • 24. Shorebirds Light footed clapper rail Photo: Monte Stinnett Courtesy: Merkel and Associates, 2009
  • 25. Courtesy: Merkel and Associates, 2009
  • 26. Restoring entire ecosystems requires patience and acceptance that habitats will evolve. Change is inevitable and management needs to be flexible.
  • 27. Mitigation for commercial development in Fremont, CA Degraded seasonal wetlands on former agricultural lands Required restoration of natural vernal pool landscape
  • 28. Development next to US FWS Refuge Two listed species with restricted distribution • VPTS and CC Goldfields Focused attention by conservation groups
  • 29. Demonstrate feasibility of establishing tadpole shrimp habitat Strict performance standards for hydrology and vegetation Implement grazing program
  • 30.
  • 31.
  • 32. INCREASED VP PLANT SPECIES IMPROVED OVER TIME
  • 33.
  • 34. Threshold requirements as performance standards do not recognize natural variability. Cows are your friends.
  • 35. Corps adopts compensatory mitigation policies Mitigation banks become of age Stormwater and LID wetlands Climate change affects everything
  • 36. Issued by Corps of Engineers: April 2008 • Sets forth regulations for mitigation compliance Mitigation banking given preference • Followed by in-lieu fee and permittee- responsible mitigation Sets forth 12 fundamental components for mitigation plans Emphasis replacement in watershed Provides for functional assessment
  • 37.
  • 38. BEFORE AFTER
  • 39. Our knowledge of wetland systems including plants, soils, and hydrology is providing the basis for a sophisticated design and public use of wetland systems in the urban environment
  • 40. Wetland restoration can achieve successful outcomes but usually not as expected Linkage between hydrology, soils, and plants is better known and allows for more sophisticated designs of drier wetlands Wetland restoration will necessarily become more complex as our demand on wetland performance increases
  • 41. Time is of the essence Pressure on wetlands is increasing Need for large scale restoration is unprecedented and immediate